Camilty Wind Farm - Partnerships for Renewables
Camilty Wind Farm - Partnerships for Renewables Camilty Wind Farm - Partnerships for Renewables
Camilty Wind Farm 11.2 Methodology Guidance 11.2.1 This assessment takes into account the requirements of the following legislation, regulations and other guidance: • Badger Protection Act (1992); • Council Directive 92/43/EEC on the Conservation of Natural Habitats and Wild Flora and Fauna (the "Habitats Directive") (1992); • Conservation (Natural Habitats &c.) Regulations 1994 (the "Habitats Regulations"); • Conservation (Natural Habitats &c.) Amendment (Scotland) Regulations 2007; • Conservation (Natural Habitats &c.) Amendment (Scotland) Regulations 2009; • Eurobats Guidelines for Consideration of Bats in Wind Farm Projects (2008); • Institute of Ecology and Environmental Management (IEEM) Guidelines for Ecological Impact Assessment (EIA) in the United Kingdom (2006); • Natural England Guidance on Bats and onshore wind turbines (2009); • Nature Conservation (Scotland) Act 2004; • Planning Advice Note 58 Environmental Impact Assessment (1999); • Planning Advice Note 60 Planning for Natural Heritage (2000); • Scottish Biodiversity List (2005); • Scottish Executive Interim Guidance on European Protected Species Development Sites and the Planning System (2001); • Scottish Planning Policy (2010); • Scottish Natural Heritage (SNH) Guidelines on the Environmental Impacts of Wind Farms and Small Scale Hydroelectric Schemes (2001); • SNH, Scottish Environment Protection Agency (SEPA), FCS Good practice during wind farm construction (2010); • UK Biodiversity Action Plan (UKBAP) (1994); • West Lothian Council Local Biodiversity Action Plan (2004); • Wildlife and Countryside Act 1981 (as amended); and • Wildlife and Natural Environment (Scotland) Act 2011 (WANE Act). Consultation 11.2.2 In October 2011 relevant consultees were each sent an Scoping letter and asked to provide comments on: • Ecological issues relating to the proposed development; and • Suitability of the proposed baseline survey, analysis and assessment methods proposed. March 2013 11-3 ES Chapter 11 Terrestrial Ecology Copyright Partnerships for Renewables Development Co. Ltd 2013 ©
Camilty Wind Farm 11.2.3 Details of the consultation responses that involved specific feedback on ecology, and further consultation arising from this, are provided in Table 11.1. 11.2.4 Additional consultation with consultees as part of the EIA Scoping process was also undertaken in July 2012, as discussed in Chapter 2: The Environmental Impact Assessment and Scoping Process. Table 11.1 Summary of Consultations and Responses Consultee Date of Consultation Summary of Response Scottish Natural Heritage (SNH) 04/10/2011 The site has historical records of badger setts and SNH recommended that a badger walkover survey be included in the scope of ecology surveys. SNH welcomed the proposal to survey using extended Phase 1 methodology and suggested that this should be followed by NVC survey of habitats of conservation interest if any of these are found on site. The area around the site hosts deep peat soils, often over 6m depth. As the depth of soils on the site will affect siting of turbines and construction methodology, SNH recommended that surveys include full peat depth survey and peat slide risk assessment. Details of the latter assessment can be found in Chapter 13. SNH confirmed that they are content with the scope and methodologies outlined in the Scoping Report. SNH 05/03/2012 SNH were generally happy with the proposed bat methodology statement and provided details of recent records of Nathusius' pipistrelles from the nearby proposed wind farm at Fauch Hill. Due to the proximity of these observations to Camilty, SNH advised the species presence on the application site could not be ruled out and that sufficient effort should be undertaken to establish presence or absence. RPS increased the survey effort for this species and included remote Anabat recording at height throughout the survey season. SNH 14/03/2012 During consultation with SNH it was agreed that instead of carrying out a full scale monitoring programme at a cluster of ponds unlikely to support great crested newts, an alternative approach would be sufficient. A design alteration was implemented by using a 300 m buffer zone around all seven ponds, which will be a no-go zone for turbines, infrastructure and any associated kind of built up structures. West Lothian Council Royal Society for the Protection of Birds (RSPB) Scottish Environmental Protection Area (SEPA) 07/09/2012 Confirmed that the scoping report was largely satisfactory, subject to the detailed advice included in the consultation responses. The EIA must have sufficient information to assess whether the proposal will have a significant effect on the qualifying interest of any Natura 2000 sites. The depth of the peat across the site must be identified in addition to distribution. 24/08/2012 The layout of the wind farm should minimise the destruction or disturbance to peat habitats. 24/08/2012 Noted that the following key issues should be addressed in the EIA process: • Disruption to wetlands including peatlands March 2013 11-4 ES Chapter 11 Terrestrial Ecology Copyright Partnerships for Renewables Development Co. Ltd 2013 ©
- Page 252 and 253: Camilty Wind Farm Plantation, would
- Page 254 and 255: Camilty Wind Farm to the south west
- Page 256 and 257: Camilty Wind Farm Moderate addition
- Page 258 and 259: Camilty Wind Farm Glasgow. A smalle
- Page 260 and 261: Camilty Wind Farm • Topic Paper 9
- Page 262 and 263: Camilty Wind Farm largely to avoid
- Page 264 and 265: Camilty Wind Farm 10.2.14 An assess
- Page 266 and 267: Camilty Wind Farm Table 10.2 Guide
- Page 268 and 269: Camilty Wind Farm Asset Importance
- Page 270 and 271: Camilty Wind Farm historic landscap
- Page 272 and 273: Camilty Wind Farm • Stage Two: de
- Page 274 and 275: Camilty Wind Farm Baseline Conditio
- Page 276 and 277: Camilty Wind Farm 10.4.2 The most s
- Page 278 and 279: Camilty Wind Farm of effect of the
- Page 280 and 281: Camilty Wind Farm Other SMs 10.5.28
- Page 282 and 283: Camilty Wind Farm is of high import
- Page 284 and 285: Camilty Wind Farm 10.5.57 The liste
- Page 286 and 287: Camilty Wind Farm 10.5.74 Some 5 km
- Page 288 and 289: Camilty Wind Farm 10.5.90 The house
- Page 290 and 291: Camilty Wind Farm 10.5.106 HB numbe
- Page 292 and 293: Camilty Wind Farm Table 10.5 Summar
- Page 294 and 295: Camilty Wind Farm included in Appen
- Page 296 and 297: Camilty Wind Farm Table 10.6 Summar
- Page 298 and 299: Camilty Wind Farm Receptor Effect D
- Page 300 and 301: Camilty Wind Farm 11 Terrestrial Ec
- Page 304 and 305: Camilty Wind Farm Consultee Date of
- Page 306 and 307: Camilty Wind Farm Bat Species 11.2.
- Page 308 and 309: Camilty Wind Farm Index (HSI) devel
- Page 310 and 311: Camilty Wind Farm Conservation Sens
- Page 312 and 313: Camilty Wind Farm Table 11.6 Design
- Page 314 and 315: Camilty Wind Farm 11.3.8 There were
- Page 316 and 317: Camilty Wind Farm 11.3.16 Marshy gr
- Page 318 and 319: Camilty Wind Farm NVC Code NVC Type
- Page 320 and 321: Camilty Wind Farm was also detected
- Page 322 and 323: Camilty Wind Farm remaining 38% wer
- Page 324 and 325: Camilty Wind Farm Badger Legal Prot
- Page 326 and 327: Camilty Wind Farm current landuse i
- Page 328 and 329: Camilty Wind Farm Valued Ecological
- Page 330 and 331: Camilty Wind Farm 11.6.8 Bat activi
- Page 332 and 333: Camilty Wind Farm Table 11.16 Areas
- Page 334 and 335: Camilty Wind Farm Table 11.18 Poten
- Page 336 and 337: Camilty Wind Farm Table 11.20 Poten
- Page 338 and 339: Camilty Wind Farm Siltbusters or eq
- Page 340 and 341: Camilty Wind Farm 11.9 Cumulative E
- Page 342 and 343: Camilty Wind Farm 11.9.22 It is con
- Page 344 and 345: Camilty Wind Farm Table 11.22 Summa
- Page 346 and 347: Camilty Wind Farm Receptor Effect D
- Page 348 and 349: Camilty Wind Farm Receptor Effect D
- Page 350 and 351: Camilty Wind Farm Receptor Effect D
<strong>Camilty</strong> <strong>Wind</strong> <strong>Farm</strong><br />
11.2.3 Details of the consultation responses that involved specific feedback on ecology, and further<br />
consultation arising from this, are provided in Table 11.1.<br />
11.2.4 Additional consultation with consultees as part of the EIA Scoping process was also<br />
undertaken in July 2012, as discussed in Chapter 2: The Environmental Impact Assessment<br />
and Scoping Process.<br />
Table 11.1 Summary of Consultations and Responses<br />
Consultee<br />
Date of<br />
Consultation<br />
Summary of Response<br />
Scottish<br />
Natural<br />
Heritage<br />
(SNH)<br />
04/10/2011 The site has historical records of badger setts and SNH<br />
recommended that a badger walkover survey be included in the scope<br />
of ecology surveys.<br />
SNH welcomed the proposal to survey using extended Phase 1<br />
methodology and suggested that this should be followed by NVC<br />
survey of habitats of conservation interest if any of these are found on<br />
site.<br />
The area around the site hosts deep peat soils, often over 6m depth.<br />
As the depth of soils on the site will affect siting of turbines and<br />
construction methodology, SNH recommended that surveys include<br />
full peat depth survey and peat slide risk assessment. Details of the<br />
latter assessment can be found in Chapter 13.<br />
SNH confirmed that they are content with the scope and<br />
methodologies outlined in the Scoping Report.<br />
SNH 05/03/2012 SNH were generally happy with the proposed bat methodology<br />
statement and provided details of recent records of Nathusius'<br />
pipistrelles from the nearby proposed wind farm at Fauch Hill. Due to<br />
the proximity of these observations to <strong>Camilty</strong>, SNH advised the<br />
species presence on the application site could not be ruled out and<br />
that sufficient ef<strong>for</strong>t should be undertaken to establish presence or<br />
absence.<br />
RPS increased the survey ef<strong>for</strong>t <strong>for</strong> this species and included remote<br />
Anabat recording at height throughout the survey season.<br />
SNH 14/03/2012 During consultation with SNH it was agreed that instead of carrying<br />
out a full scale monitoring programme at a cluster of ponds unlikely to<br />
support great crested newts, an alternative approach would be<br />
sufficient. A design alteration was implemented by using a 300 m<br />
buffer zone around all seven ponds, which will be a no-go zone <strong>for</strong><br />
turbines, infrastructure and any associated kind of built up structures.<br />
West Lothian<br />
Council<br />
Royal Society<br />
<strong>for</strong> the<br />
Protection of<br />
Birds (RSPB)<br />
Scottish<br />
Environmental<br />
Protection<br />
Area (SEPA)<br />
07/09/2012 Confirmed that the scoping report was largely satisfactory, subject to<br />
the detailed advice included in the consultation responses. The EIA<br />
must have sufficient in<strong>for</strong>mation to assess whether the proposal will<br />
have a significant effect on the qualifying interest of any Natura 2000<br />
sites. The depth of the peat across the site must be identified in<br />
addition to distribution.<br />
24/08/2012 The layout of the wind farm should minimise the destruction or<br />
disturbance to peat habitats.<br />
24/08/2012 Noted that the following key issues should be addressed in the EIA<br />
process:<br />
• Disruption to wetlands including peatlands<br />
March 2013 11-4 ES Chapter 11<br />
Terrestrial Ecology<br />
Copyright <strong>Partnerships</strong> <strong>for</strong> <strong>Renewables</strong> Development Co. Ltd 2013 ©